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Serim - 2.05.6 <br />to decreaze az available soluble chemical constiruenu are depleted and chemical concentrations in the <br />• mine water and the exposed rock reach equilibrium Gradual filling of the mine workings will also <br />Gave a beneficial water quality effett, displacing oxygen and reducing the oxidation potential az <br />flooding of the abandoned workings occurs. <br />As described in Section 2.4.7, Hydrologic Description, ground water in both the permit and adjacent <br />areaz is a weak calcium-sulfate or sodiurrrsulfate chemical type. Increazes in both sodium and sulfate <br />constiruenu will not change ground water chemistry although they could result in a shift toward a <br />more dominant ground water type. While various chemical constituenu of the ground water may <br />increase az a result of mine drainage, these increases will not effect ground water use. Due to the <br />limited volume of ground water drainage relative to total flows within the ground water bazin, minor <br />changes in ground water chemistry and levels of certain cotutiruenu are not expected to significantly <br />effect overall ground water quality. Use of ground water from the permit and adjacent areaz is very <br />limited due to the availability of more accessible and higher quality surface water sources. <br />OMI's planned nesting and related attivities are not expected to have any significant long-term effect <br />on recharge, storage, or discharge relationships. As described in Section 2.04.7, Hydrologic <br />Description, recharge within the ground water basin occurs primarily along the outcrop of the vazious <br />stratigraphic uniu az a result of direct precipitation and infiltration in outcrop areas. OMI's <br />operations are both limited in areal extent and are not located within any major recharge area. <br />Drainage of the stored mine water system during mining operations will effect ground water storage <br />relationships. This effett, however, will be localized and temporary. Upon completion of operations <br />and mine reclamation and closure, ground water will once again accumulate in the mine workings and <br />ground water storage relationships will be reestablished. Discharge relationships will ako be <br />minimally effected with some temporary reduction in downgradient ground water flows az a result of <br />• filling of the underground mine workings az well az localized alterations in ground water flow <br />patterns. The quantity of ground water discharge which will be effetted u a relatively small <br />percentage of the total volume within the ground water basin. <br />The existing Somerset and Sanborn Creek mine workings and proposed Elk Creek workings progress <br />down-dip from the mine portals and mine drainage u controlled during active operations, so there is <br />little or no potential for direct gravity discharge of water from the mine. On completion of mirtirtg <br />and related activities, however, mine drainage control operations will cease and portions of the mine <br />workings (especially the mine workings furthest down-dip) are expected to gradually fill az continuous <br />ground water inflows discharge to the mined-out areas. Bazed on the Jack of any significant base-flow <br />in Elk Creek and absence of shallow ground water in test borings in the portal area, the natural water <br />table is below the portal elevation and mine water discharge from the E& Creek Mate portals is not <br />anticipated. To assure that there will not be any significant discharge from the mine openings <br />following cessation of active mining operations and mine closure, OMI will sea] and bacldill the mine <br />portals. Sealing prattices are discussed in Sections 2.05.4, Reclamation Plan, and later in this section <br />under the heading, Reclamation of 1vLne Disturbance Areas. Water will not be diverted or discharged <br />into any other underground mine in conjunttion with OMI's ongoing mining and reclamation <br />operations. <br />The only anticipated potential ntirtirtg-related impact on water righu and use would be minor <br />reductions in flows to the North Fork due to mine water supply whdrawa]s az previously addressed <br />under the sub-heading, MInor Reductions in Surface Flows and Alteration of Surface Flow Patterns <br />Due to Operation of Sedimentation Structures and Flow Reductions Due to 1vLne Water Supply <br />Withdrawals. As noted in the referenced discussion, both the average annual and ma~**~ttm <br />anticipated water supply withdrawal rates represent a very small percentage of total flow volume for <br />. the North Fork Mme drainage, which does not result in any reduction in surface flows due to the <br />lack of a direct hydraulic connection, will probably result in some variable discharge of excess mine <br />water to the surface system, effectively augmenting surface flows on a year-rotmd bazis. While mining <br />and related subsidence may impact overlying perched aquifers and any associated seeps or springs, as <br />previously discussed under the sub-heading of, Drainage of Seeps and Springs, water righu <br />PR04 2.05-96 Revised May 2001 <br />